Membrane-Confined Iron Oxychloride Nanocatalysts for Highly Efficient Heterogeneous Fenton Water Treatment

被引:209
作者
Zhang, Shuo [1 ]
Hedtke, Tayler [1 ]
Zhu, Qianhong [1 ]
Sun, Meng [1 ]
Weon, Seunghyun [1 ,2 ]
Zhao, Yumeng [1 ,3 ]
Stavitski, Eli [4 ]
Elimelech, Menachem [1 ]
Kim, Jae-Hong [1 ]
机构
[1] Yale Univ, Dept Chem & Environm Engn, New Haven, CT 06511 USA
[2] Korea Univ, Sch Hlth & Environm Sci, Seoul 02841, South Korea
[3] Harbin Inst Technol, State Key Lab Urban Water Resource & Environm, Harbin 150090, Peoples R China
[4] Brookhaven Natl Lab, Natl Synchrotron Light Source 2, Upton, NY 11973 USA
基金
美国国家科学基金会;
关键词
membrane reactor; iron oxychloride; hydroxyl radicals; kinetics; confinement effect; HYDROXYL RADICALS; PHOTO-FENTON; BISPHENOL-A; DEGRADATION; CATALYST; OXIDE; NANOPARTICLES; OXIDATION; REMOVAL; H2O2;
D O I
10.1021/acs.est.1c01391
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Heterogeneous advanced oxidation processes (AOPs) allow for the destruction of aqueous organic pollutants via oxidation by hydroxyl radicals ((OH)-O-center dot). However, practical treatment scenarios suffer from the low availability of short-lived (OH)-O-center dot in aqueous bulk, due to both mass transfer limitations and quenching by water constituents, such as natural organic matter (NOM). Herein, we overcome these challenges by loading iron oxychloride catalysts within the pores of a ceramic ultrafiltration membrane, resulting in an internal heterogeneous Fenton reaction that can degrade organics in complex water matrices with pH up to 6.2. With (OH)-O-center dot confined inside the nanopores (similar to 20 nm), this membrane reactor completely removed various organic pollutants with water fluxes of up to 100 L m(-2) h(-1) (equivalent to a retention time of 10 s). This membrane, with a pore size that excludes NOM (>300 kDa), selectively exposed smaller organics to (OH)-O-center dot within the pores under confinement and showed excellent resiliency to representative water matrices (simulated surface water and sand filtration effluent samples). Moreover, the membrane exhibited sustained AOPs (>24 h) and could be regenerated for multiple cycles. Our results suggest the feasibility of exploiting ultrafiltration membrane-based AOP platforms for organic pollutant degradation in complex water scenarios.
引用
收藏
页码:9266 / 9275
页数:10
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